Our Purdue research team is in the midst of a major RAPID response Water Pipe Safety study that will have national impact and we truly need your help. We have kicked off a 28 day fundraiser to raise funds for completing this project: Visit this research page here.
Chemicals are being emitted from the cured-in-place-pipe (CIPP) installation while Purdue student Kyungyeon Ra conducts air sampling.
Brandon, John, Nadya, Mabi, Kyungyeon, Emily and I are working to identify the chemicals emitted from the most popular water pipe repair procedure in the USA called cured-in-place-pipe (CIPP). We are Purdue undergraduate and graduate students, faculty, staff.
The CIPP process is used to create a new pipe within an existing broken pipe. When used, chemicals are emitted into workspaces and the nearby air. Much public talk has been on styrene, a carcinogen and common CIPP ingredient. Sometimes when sewer pipes are repaired, chemicals emitted from CIPP can make their way into nearby homes, schools, and office buildings [See a list of some incidents below].
There has been no independent or public study to document the suite of chemicals emitted into the air or their human health, safety, or environmental risks. Thousands of people work in the CIPP industry every day.
How Can You Help?
Please consider donating through our tax-deductible crowdfunding project here: https://crowdfunding.purdue.edu/project/2768. Any amount is greatly appreciated. Our ultimate goal is $24,000 to pay for expenses we are personally carrying already for this project and expenses for additional supplies and making the data public. We will keep you up to date on our activities and results.
Please share our story and our donations page on social media. The more people who know about this effort the better, especially for an awareness of the CIPP process which may be used in street near you, your friends, or family.
Team members conducted a field site walkthrough the day before CIPP installations began. Our initial air testing indicated a need to protect ourselves by wearing full-face mask respirators.
With RAPID seed funding from the National Science Foundation (about $21,000 direct costs) and a previous fundraising effort ($1,350) we’ve been able to make A LOT of progress. [A special thanks to our 20 remarkable donors]. We are still in need of funds because early in our project we unexpectedly discovered potentially serious unaddressed CIPP safety risks. We had to spend more money on safety and testing equipment than we expected. Once this RAPID response study is completed, we will disseminate information to the public. Our reports will be Open-Access and freely available. By contributing to this study you will enable us to investigate this public safety issue.
Purdue Professor Boor standing near one of the CIPP’s being installed
Recently we returned from air testing at a California CIPP field site. We are analyzing more than 200 samples to ascertain what chemicals were emitted and compare their levels to human health safety standards. We also have more than 300,000 air sampling data points from this field work we are working to better understand. As part of this study we are also examining where the chemicals went when they were emitted.
Who We Are
The project team involves myself along with Purdue Professors Brandon Boor (Civil Engineering), John Howarter (Materials Engineering), Laboratory Director Nadya Zyaykina (Civil Engineering/Environmental and Eco Engineering), graduate students Mabi Teimouri (Civil Engineering), Kyungyeon Ra (Environmental and Eco Engineering), and undergraduate student Emily Conkling (Environmental and Eco Engineering).
Our field work has been intense and we needed months to prepare and practice for it. We have been working countless hours for this project, volunteering time, even working through many weekends just to obtain the air samples and analyze them.
The CIPP installations we monitored were located in California. We had to drive our specially constructed equipment 4,500 miles to conduct the air testing. We worked multiple long 12-15 hour days just to collect the samples.
Presented in the Health Sciences seminar was an investigation of (1) the acute toxicity of chemicals spilled into the environment from the Freedom Industries tank site to Daphnia magna, a common aquatic freshwater organism, and (2) the spreadsheet based Excel tool that utilities and government agencies can use to design water heater decontamination guidance in the aftermath of drinking water contamination incidents. The presentation is available for download here: Health Sciences Seminar: Elk River Chemical Spill.
Chemical Spill Toxicity Analysis for an Aquatic Freshwater Organism
The toxicological investigation was conducted by graduate student Caroline Novy and Professor Donald Beebe from University of South Alabama and Dr. Whelton at Purdue University. Their investigation involved exposing Daphnia magna, also known as a water flea, to various concentrations of Crude MCHM provided to the researchers in 2014 by the chemical company, liquid obtained from the Freedom Industries tank (a mixture of Crude MCHM and Stripped PPH), and analytical grade 4-MCHM from TCI America. [Analytical grade 4-MCHM has been referred to as pure MCHM because it only contains cis/trans isomers, not other components present in the tank liquid or Crude MCHM]
During this study the researchers determined the effective concentration where 50% of the daphnid population studied exhibited adverse effects (visible by sight) during a 48 hour exposure period. This is known as the EC50 value. Also determined was the no observed effect concentration (NOEC) for a 48 hour exposure period for each liquid where daphnids were also not visibly adversely affected. The daphnid acute toxicity testing protocols described by the chemical manufacturer in 1998 and the US Environmental Protection Agency (EPA) were applied in this study.
The researchers found Crude MCHM provided by the chemical manufacturer in 2014…
1. Was more acutely toxic than the Crude MCHM the manufacturer last tested in 1998, and
2. Was more acutely toxic than pure MCHM, the analytical standard used in animal studies.
The researchers have postulated that differences between the toxicity of these liquids is likely due to differences in product chemical composition. Each liquid, while containing some of the same ingredients as the other liquids tested, exhibited different acute toxicity thresholds for this aquatic organism. It seems the daphnid toxicity data listed on the chemical manufacturer’s material safety data sheet provided to the responders in 2014 was not representative of the product available in 2014.
Follow-up environmental sampling and monitoring by Freedom Industries’s contractors determined 4-MCHM was present at levels that exceeded daphnid acute toxicity thresholds found in the present study and those previously reported by the chemical manufacturer. To date, 4-MCHM has been detected as high as 190 mg/L in water collected from the Etowah Terminal tank site by Freedom Industries’s contractors.
The Purdue University and University of South Alabama researchers will continue to examine the sublethal effects of the exposure to daphnids as well as other organisms. Work is expected to be completed in 2016. Several other organizations continue to conduct toxicological examinations on the chemicals spilled in West Virginia. These include the US National Toxicology Program, US Geological Survey, Northeastern University, West Virginia University, and Fontebonne University. Toxicity testing has also been conducted by scientists hired by lawyers representing the ongoing class-action lawsuit.
Water Heater Flushing Model, version 1 (Released 8/2015)
Also presented at the Health Sciences seminar were field and pilot scale testing results decontaminating residential water heaters. Researchers include Professor Whelton, graduate student Karen Casteloes, and undergraduate student Jake Hawes of Purdue University along with Professor Randi Brazeau at the Metropolitan State University of Denver.
The researchers flushed a conservative chemical contaminant from two water heaters and found that the Microsoft Excel based model developed by Casteloes et al. (2015) and published in a paper here Environmental Science: Water Research and Technology(<== free paper download ) closely predicted water heater chemical removal effectiveness. This is important because in the wake of the Elk River Chemical Spill officials lacked guidance on how residents should clean their contaminated water heaters. In-home testing conducted by Whelton’s research team and West Virginia University revealed water heater decontamination in accordance with utility and state guidance was sometimes ineffective. ==>Water utilities and government agencies now have a tool they can use in their decision-making process.
This model became available to water utilities and government agencies in August 2015 and was presented to federal and state agencies as well as major water utilities at a National Experts Water Industry Workshop held August 2015 in Washington, D.C. This workshop was part of a ongoing project, funded by the Water Research Foundation and led by CEC. CEC is further developing plumbing system flushing guidance in response to and avoid drinking water health advisories for water utilities. The MS Excel file/model (.xlsx file type) developed by Casteloes et al. (2015) can be found here: PURDUE Water Heater Flushing Model v1 (Aug2015)
Additional work by the Purdue University and Metropolitan State University researchers is ongoing to evaluate different contamination and decontamination scenarios and decontamination aides.
On August 26, Dr. Whelton delivered the Fall 2015 conference keynote address and lunch time presentation for the Alliance Indiana of Rural Water meeting in Fort Wayne, Indiana. The Alliance represents more than 800 drinking water and wastewater utilities in Indiana and provides an excellent service to its members and partners.
Dr. Whelton’s key note conference presentation focused on Community Resilience specifically as it pertains to the 2014 Chemical Spill in West Virginia and many subsequent chemical spills that have occurred across the U.S. (Key Note Presentation). The lunch time presentation included a discussion of the complexity of plastic drinking water plumbing systems, test standard deficiencies, and results from his team’s bench- and field-scale research activities (Lunch Presentation). More information about the chemical spill can be found here. New results from the team’s plastic plumbing system research can also be found by typing the word “PEX” into the website search bar.
On January 9 2014, 300,000 people in the Charleston, West Virginia area were directed not to use there licorice smelling tap water… touching off one of the largest acute drinking water disasters in US history.
Freedom Industries, Inc. and it’s staff stored tens of thousands of gallons of a coal washing liquid within feet from the Elk River. Their storage tanks were 1.5 miles upstream of a regional drinking water treatment facility’s intake. Because Freedom Industries and its staff failed to maintain their above ground storage tanks (catastrophic corrosion occurred), more than 10,000 gallons of a liquid mixture of compounds called Crude MCHM and Stripped PPH entered the water supply on or near January 9.
The water company, West Virginia American Water, chose to draw this tainted water into it’s water treatment facility, increased their chemical dosages in an attempt to remove the chemicals so they could avoid shutting down their water system. This could have resulted in water distribution system depressurization.
Late afternoon on January 9, the water company discovered their treatment approach was ineffective and the Do Not Use drinking water order was issued by the Governor with support of the water company. Several hours later President Obama declared the incident a federal disaster.
It was Unprecedented
The scale of the acute drinking water contamination incident was unprecedented.
Nine counties were affected, 15% of the West Virginia’s population. Businesses and schools were shutdown, hospitals and other critical care facilities were faced without distributed drinking water.
Contaminated water resided in more than 2,200 miles of water pipes, more than 100 drinking water storage tanks, and upwards of 90,000 building plumbing systems. Residents sought medical attention at hospitals and from their physicians after experiencing chemical burns and inhalation issues.
The main ingredient in the spilled liquid was 4-MCHM, 4-methylcyclohexane methanol, but a number of other ingredients were known to be present as well.
The MSDS’s which responders relied upon for decisions, found to be inaccurate later on, were missing key health impact data and many of the chemicals spilled were not listed on any MSDS. [12 days after the spill Freedom Industries would disclose additional chemicals being spilled into the Elk River that they failed to notify anyone about.]
The Crude MCHM Safety Data Sheet listed health hazards and some of the chemicals spilled into the Elk River, but not all. Stripped PPH, a second liquid product with a separate data sheet, was also mixed into the spilled liquid. Freedom Industries did not disclose it was present until 12 days after the spill.
Arrival in West Virginia and the National Science Foundation
After my volunteer student and faculty team drove from Alabama into the area in January 2014 to help the community respond we quickly realized the scale of the disaster. It was fate that we were able to team up the West Virginia Clean Water Hub (Rob Goodwin) and People Concerned About Chemical Safety (Maya Nye) to help residents decontaminate their homes, testing their water, and ultimately redesigning the flushing method issued by the responders.
By chance we crossed paths with Krysta Bryson, a PhD student at Ohio State University, and also a West Virginian who’s family lived in the affected area. She, on her own dime, began documenting the incident as well as the experiences of residents with video, cell phone audio recorder, and camera. We teamed up with her and she since established a West Virginia Water Crisis blog that still is updated today. Check it out here.
Volunteer university team on January 17, 2014 near the Kanawha River, Charleston, West Virginia: (Left to Right) Jeff Gill (grad student), Keven Kelley (grad student), Prof. Andrew Whelton, Prof. Kevin White, Matt Connell (grad student), LaKia McMillan (grad student)
Upon returning to our home we were inundated with emails and telephone calls from residents affected by the spill. Together, we created a blog post with answers to common questions and simultaneously published it on Krista Bryson’s blog. The Q&A does not include every question we received, but the most common. We continue to receive questions.. in March 2015 we received questions from residents affected by the spill.
In January, the US National Science Foundation too recognized the unprecedented scientific need, saw the impact firsthand, and stepped in. They providing emergency funding to my team on the ground, Krista Bryson and her advisor at Ohio State University. NSF also authorized rapid research projects at West Virginia University, Ohio State University, University of Memphis, and Virginia Tech. Below is a video that describes some of the research that we have conducted.
The NSF rapid funding has enabled my team and collaborators to assist West Virginians, the utilities, and State and Federal agencies number of ways. We have made a variety of discoveries (some described below) and have several more in the pipeline. Without NSF funding I am pretty sure that no other agency would have stepped in to fund the necessary science for this disaster.
NSF is funded by Federal tax dollars (appropriated by the legislative branch). Without this funding I can assure you many questions West Virginians asked would never have been answered based on a review of past chemical spill responses. Our discoveries have the potential to help Americans across the US be better protected and prepared for a similar (or more severe) event. Our results also have direct relevance to communities affected by chemical spills outside the US. Science has no borders.
Graduate students Keven Kelley and LaKia McMillan collect and analyze contaminated tap water in one of the homes we visited during our rapid response. Results of this testing were described in a FREE report published by the Journal Environmental Science and Technology journal overseen by the American Chemical Society.
The following people and organizations have contributed in some way to our NSF funded research. This includes assistance conducting our investigation, feedback about our results, scientific input about testing or results, and clarification about events or data.
Residents and businesses affected by the spill
Purdue University: Prof. Andrew Whelton, Karen Casteloes, Xiangning Huang
University of South Alabama: Prof. Kevin White, Prof. Rajarshi Dey, Prof. Alex Beebe, Prof. Anne Boettcher, LaKia McMillan, Keven Kelley, Matt Connell, Jeff Gill, Caroline Novy, Mahmoud Alkhout, Frederick Avera, Coleman Miller
University of New Mexico: Prof. Jose Manuel Cerrato
Kanawha Charleston Health Department: Dr. Rahul Gupta
People Concerned About Chemical Safety: Maya Nye
West Virginia Clean Water Hub: Rob Goodwin
Downstream Strategies, Inc.: Evan Hansen
US Chemical Safety Board
West Virginia American Water Company
Eastman Chemical Company
Charleston Sanitary Board
State of West Virginia
Ohio State University: Krista Bryson
West Virginia University: Prof. Jennifer Weidhass
Metropolitan University of Denver: Prof. Randi Brazeau
AWWA: Alan Roberson, Dr. Kevin Morley
National Resources Defense Council: Erik Olson
West Virginia’s Government Stepped Forward Requesting Assistance
When were were in Charleston conducting water sampling and helping residents flush their plumbing systems, we approached the Governor’s staff with our findings that residents were becoming ill by flushing and that decisions being made were not based on science. Shortly after the NSF stepped in the West Virginia Governor’s office then contacted my team for assistance. In response, I called some good friends who recommended I contact Jeffrey Rosen, president of Corona Environmental Consulting LLC. After a brief conversation he and I flew to West Virginia, met with the State of West Virginia executive staff, and formed the West Virginia Testing Assessment Project (WVTAP).
WVTAP consisted of scientists and engineers from the United States, United Kingdom, and Israel. Team members had expertise in toxicology, risk assessment, statistics, environmental chemistry and microbiology, water treatment and distribution, analytical chemistry, environmental monitoring and sampling, sensory analysis, and media relations. More importantly though, this “project” was intended to answer critical questions West Virginians were demanding be answered regarding drinking water safety, and odor that no state or federal agency had acted upon before.
While WVTAP’s work ended in June 2014, my university team has continued it’s efforts and many more researchers have stepped-in funded through various agencies.
The team included Dr. Andrew Whelton as well as Jeffrey Rosen, Dr. Jennifer Clancy, Tim Clancy, Dr. Tim Bartrand (CEC), Dr. Michael McGuire (McGuire, Inc.), Dr. Mel Suffet (UCLA), Dr. Craig Adams (Utah State Univ.), Dr. Michael Dourson, Jacqueline Patterson (TERA), Dr. Andy Eaton, Duane Luckenbill, Charles Neslund, (Eurofins). Others who participated include Paul Painter (ALS), Drs. Paul Rumsby (WRc), James Jacobus (MN DoH), Shai Ezra (Israel National Water Co Ltd), Stephen Robers (Univ. Florida)
Several other organizations initiated efforts help understand the chemical spill’s impact. For example, the United States National Toxicology Program initiated federally funded research to determine the health impacts associated with exposure to several of the chemicals in West Virginia’s drinking water. The United States Geological Survey reported on their drinking water and river water sampling efforts. Various universities have published chemical modeling and laboratory testing research on some of the chemicals in the drinking water and river. These results are explained below along those from with many other organizations.
A Few Major Discoveries from the Chemical Spill (so far…)
Numerous scientific reports have been released by various organizations since January 2014 regarding the chemical spill in West Virginia. Here are some quick observations of their findings. I did not include any of the new discoveries my team will release in the next couple months.
The chemical methyl 4-methylcyclohexanecarboxylate (MMCHC), an ingredient in the spilled liquid, was found in the drinking water by the US Geological Survey research six weeks after the spill. Responders did not know this chemical was present. Unlike the other chemicals 4-MCHM, PPH, and DiPPH, no safe drinking water exposure level was established for this compound.
Toxicologists assumed the toxicity of Crude MCHM is the same as the toxicity of analytical standard pure 4-MCHM. The analytical standard however has a different trans- / cis- isomer ratio than the crude MCHM. Researchers have recently discovered the volatility and potential for each isomer to sorb to organic materials differs substantially. Our testing indicates the Crude MCHM is actually much more toxic to an aquatic organism than analytical grade 4-MCHM (results coming soon). This difference is due to the chemical differences between Crude MCHM (mixture of many compounds) and analytical grade 4-MCHM (only contains trans- / cis- isomers).
Chemicals present in Crude MCHM (one of the two major liquids present in the spilled liquid) volatilize into the air when contaminated drinking water is at room temperature and moreso when it is heated. Flushing hot water from a plumbing system exposed residents to higher chemical levels than cold water flushing. Side-effects due to inhalation exposure occurred at 4-MCHM levels well below CDC’s 1 ppm safe drinking screening level. No inhalation toxicity testing has been conducted.
The EPA developed an ambient air monitoring method for 4-MCHM and deployed it at the Freedom Industries site in late 2014. Some 4-MCHM was detected at that time, but well-below their 0.01 ppm-v air screening level. No air monitoring was conducted inside buildings when contaminated water was flushed from the pipes or used routinely after 4-MCHM levels were below CDC’s 1 ppm safe 4-MCHM screening level.
Three different organizations told the affected population to apply three different building plumbing system flushing approaches. None of them were developed based on either science or plumbing system design.
The plumbing system contaminated water flushing guidance issued by the water company and approved by the State and Federal agencies ignored the health risks associated with inhalation exposure. As a result, residents became ill by following guidance issued to them by the agencies responding to the spill. [We will have results shortly that describe the indoor air levels experienced by residents]
Plumbing system flushing did not reduce 4-MCHM levels for all homes. It is unclear how this guidance was designed as there is no documentation for it’s design. The responders stated objective of plumbing system flushing was to reduce 4-MCHM below 1000 parts per billion. Based on our testing, certain homes were more likely not be decontaminated compared to others.
A 2015 study we conducted using a mass balance model, enabled us to determine that the plumbing system flushing guidance did not consider basic factors such as the size of the water heater needed to flush, low-flow fixtures, and typical building plumbing system designs. In fact, homes with water saving fixtures and large water heaters were more likely to not be decontaminated than other homes. The model we developed was provided to water companies so they can use it following the next incident.
You can detect the licorice odor when contaminated drinking water contained less 0.15 parts per billion concentration of Crude MCHM and about 8 parts per billion of 4-MCHM.
The Center for Disease Control and Prevention’s (CDC) 4-MCHM screening level of 1000 parts per billion was inadequate and did not protect public health for all populations under all water use conditions.
The State of West Virginia drinking water screening level (health limit) of 10 parts per billion for 4-MCHM was adequate to protect public health for all populations under all water use conditions.
4-MCHM was detected 400 miles downstream after the spill on the Ohio River. Water utilities 600 miles downstream took preventative measures.
Despite a variety of chemicals being spilled from the Freedom Industries tank site, river water testing did not consider any chemical other than 4-MCHM.
One month after the spill resident’s drinking water still contained 4-MCHM at low levels because the water company filters remained contaminated. Early on the incident response, the water company, at a hearing of the state legislature, claimed their filters “were not compromised.” Filters were replaced by the water company more than 2.5 months after the spill. Residents were provided contaminated water during this time.
At high doses, animals exposed to ingredients of the spilled liquid experience acute health impacts.
Initially there were 50 lawsuits against Freedom Industries, Inc. (company who’s tanks ruptured), West Virginia American Water (water company), Eastman Chemical Company (chemical supplier). At present, the number is unclear, but a class-action suit is pending.
The water company is still considering installing online chemical analysis monitoring equipment for the Elk River.
Several former Freedom Industries employees have been indicted by the federal government under the direction of the US Attorney Booth Goodwin. Please bargains were obtained from these individuals. Sentencing has not taken place yet.
The Chemical Safety and Hazard Investigation Board (CSB) is still investigating.
LIST OF PRINT RESOURCES DESCRIBING VARIOUS ASPECTS OF THE SPILL’S IMPACT BY US AND OTHER ORGANIZATIONS
Brief abstracts have been pasted below. Download the full reports at the links provided.
WEST VIRGINIA TESTING ASSESSMENT PROJECT (WVTAP)
The State of West Virginia funded an independent science and engineering research team to assist them in February 2014. There were three major objectives to their project: Objective #1 was to convene an international panel of experts to examine the West Virginia safety factor applied to their 10 part per billion (ppb) MCHM drinking water screening level. These individuals were be health risk assessment experts recruited from the scientific community. Objective #2 was to determine the drinking water odor threshold for MCHM. This action was important because it was possible people could detect MCHM odors at concentrations less than sensitive laboratory instruments can detect. This effort was be completed by some of the most well-known drinking water odor experts in the world. Objective #3 was to conduct a focused residential drinking water sampling field study. The collected data were then used to support the design of a larger more comprehensive program for the nine counties affected.
WVTAP Final Report, appendices, press releases, and statements. Access this report here.
US NATIONAL TOXICOLOGY PROGRAM
In response to the request by the Centers for Disease Control and Prevention/Agency for Toxic Substances and Disease Registry for additional toxicology data on chemicals associated with the Elk River spill in West Virginia, NTP is conducting a number of studies of relatively short duration to provide information relevant to the potential exposures of the Charleston residents. Access their data here.
High throughput screening: Assays to derive information about cellular and molecular targets and use for predicting potential biological effects. Update from Dec. 2014. Structure activity relationship: A computational assessment that uses chemical structure to predict toxicological and biological properties. Update from Dec. 2014. Bacterial mutagenicity: Short-term tests to evaluate DNA damage in the bacteria S. typhimurium and E. coli caused by exposure to a chemical. Ongoing as of April 2015. Zebrafish developmental effects: Short-term study to evaluate developmental effects in a vertebrate model system. Ongoing as of April 2015. Nematode (Caenorhabditis elegans) toxicity: Short-term study to evaluate chemical effects over the life span of the organisms. Update from Mar. 2015. Rat toxicogenomic (5-day): Short-term toxicity studies that identify subtle effects of a chemical on molecular processes in the liver and kidney and examine toxic effects in blood and damage to DNA (genetic toxicity). Update from Feb. 2015. Irritation/ sensitization: Assays to evaluate the ability of chemicals to cause skin inflammation by directly damaging cells (irritation) or by inducing an immune response known as allergic hypersensitivitiy or contact allergy. Ongoing as of April 2015. Rat prenatal developmental toxicity (teratology): A study where rats are exposed to a chemical throughout pregnancy to determine if it produces adverse effects on the developing fetus. Update from Dec. 2014.
AFTER ACTION REVIEW CONDUCTED BY THE STATE OF WEST VIRGINIA
After Action Review, Emergency Response to January 9, 2014 Freedom Industries Chemical Leak. Peter Markum, Jimmy Gianato, James Hoyer. State of West Virginia. Access this report here.
PEER-REVIEWED JOURNAL ARTICLES
Decontaminating Chemically Contaminated Premise Plumbing Systems. Casteloes, K.S., Brazeau, R.H., Whelton, A.J. Environmental Science: Water Research and Technology, 2015, Published: August, 2015 DOI: 10.1080/19392699.2015.1048335.
Recent large-scale drinking water chemical contamination incidents in Canada and the U.S. have affected more than 1,000,000 and involved disparate premise plumbing decontamination approaches. In this study, past premise plumbing decontamination approaches were reviewed and a mass balance water heater model was developed and tested. Organic contaminants were the sole focus of this work. Thirty-nine contamination incidents were identified and contaminants had a wide range of physiochemical properties [i.e., log Kow, water solubility, vapor pressure]. Minimal data was available pertaining to flushing protocol design and effectiveness. Results showed that premise plumbing design, operational conditions, contaminants present and their properties, as well as building inhabitant safety have not been fully considered in flushing protocol design. Results indicated that flushing could decontaminate some, but not all plumbing systems. Several modeling scenarios showed contaminant levels exceeded drinking water health limits after flushing following recent large-scale water contamination incidents. Water saving fixtures and devices, water heater size, and flow rate affected contaminant removal efficiency. Modeling did not consider service lines or piping. This study provides a first step in the development of science based premise plumbing flushing protocols for organic contaminants.
Residential Tap Water Contamination Following the Freedom Industries Chemical Spill: Perceptions, Water Quality, and Health Impacts. Andrew J. Whelton, LaKia McMillan, Matt Connell, Keven M. Kelley, Jeff P. Gill , Kevin D. White, Rahul Gupta, Rajarshi Dey, and Caroline Novy (Purdue University, University of South Alabama, Kanawha Charleston Health Department). Environmental Science and Technology. 2015, 49 (2), pp 813–823.
During January 2014, an industrial solvent contaminated West Virginia’s Elk River and 15% of the state population’s tap water. A rapid in-home survey and water testing was conducted 2 weeks following the spill to understand resident perceptions, tap water chemical levels, and premise plumbing flushing effectiveness. Water odors were detected in all 10 homes sampled before and after premise plumbing flushing. Survey and medical data indicated flushing caused adverse health impacts. Bench-scale experiments and physiochemical property predictions showed flushing promoted chemical volatilization, and contaminants did not appreciably sorb into cross-linked polyethylene (PEX) pipe. Flushing reduced tap water 4-methylcyclohexanemethanol (4-MCHM) concentrations within some but not all homes. 4-MCHM was detected at unflushed (<10 to 420 μg/L) and flushed plumbing systems (<10 to 96 μg/L) and sometimes concentrations differed among faucets within each home. All waters contained less 4-MCHM than the 1000 μg/L Centers for Disease Control drinking water limit, but one home exceeded the 120 μg/L drinking water limit established by independent toxicologists. Nearly all households refused to resume water use activities after flushing because of water safety concerns. Science based flushing protocols should be developed to expedite recovery, minimize health impacts, and reduce concentrations in homes when future events occur.
The crude MCHM chemical spill in Charleston, W.Va. Rosen, Jeffrey S.; Whelton, Andrew J.; McGuire, Michael J.; Clancy, Jennifer L.; Bartrand, Timothy; Eaton, Andrew; Patterson, Jacqueline; Dourson, Michael; Nance, Patricia; Adams, Craig. Journal of the American Water Works Association. September 2014. Volume / Number: 106, Number 9, 65-74. Access this report here.
The Elk River spill is a call to action for all water utilities with hazardous chemicals in close proximity to their source water. Regardless of the regulations and responsibilities of state and federal regulators, water utilities have responsibilities and liabilities that should prompt action to identify possible chemical threats.
An unwanted licorice odor in a West Virginia water supply. McGuire, Michael J.; Rosen, Jeffrey; Whelton, Andrew J.; Suffet, I.H. Journal of the American Water Works Association. June 2014. Volume / Number: 106, Number 6, 72-82. Access this report here.
After the headline-making chemical spill into West Virginia’s Elk River in January 2014 affected nine counties and left residents with a licorice odor in their tap water, an expert-panel study was conducted to better understand the spill’s odor characteristics.
A network analysis of official Twitter accounts during the West Virginia water crisis. Morgan C. Getchell, Timothy L. Sellnow.Computers in Human Behavior, 2015, Published: July 26, 2015 DOI: 10.1016/j.chb.2015.06.044. Access the report here.
Online networks using Web 2.0 technologies have proven useful for communication among all parties involved in managing crises. These networks rapidly disseminate information allowing for coordination among organizations responding to the needs of those whose safety and wellbeing are threatened by the crisis and its aftermath. This study provides a network analysis of official Twitter accounts activated during the Charleston, West Virginia, water contamination crisis in 2014. The city’s water supply was rendered unfit for drinking or bathing after 7500 gallons of a toxic chemical leaked into the Elk River. The network created by the 41 Twitter accounts associated with the West Virginia water contamination lacked density, contained several isolates, exchanged information quickly (geodesic distance diameter), and contained both national and local accounts. The lack of density indicates limited exchange of information, particularly between national and federal accounts. The rapid dissemination of the information that was shared and the fact that some accounts did bridge the local and national gap, however, show the positive potential for such networks in responding to crises.
Partitioning Behavior of 4-Methyl Cyclohexane Methanol in Two Appalachain Coal Preparation Plants. Aaron Noble, Y. Thomas He, Paul Ziemkiiewciz. International Journal of Coal Preparation and Utilization, 2015, Published: June 14, 2015 DOI: 10.1080/19392699.2015.1048335. Access the report here.
To assess the environmental fate and partitioning of 4-methyl cyclohexane methanol (MCHM), plant-wide water sampling surveys were conducted at two Appalachian coal preparation plants. Samples were recovered from various streams within the coal preparation plants as well as environmental discharges, including impoundment drains and groundwater monitoring wells. The results indicate measurable MCHM concentrations are only found immediately around the flotation circuit (feed, concentrate, and tailings). Samples from downstream units, including thickeners, impoundments, and discharge points show no measurable concentration of MCHM implying that volatilization and adsorption are strongly influencing the measurable concentration.
Self-Reported Household Impacts of Large-Scale Chemical Contamination of the Public Water Supply, Charleston, West Virginia, USA. Charles P. Schade , Nasandra Wright, Rahul Gupta, David A. Latif, Ayan Jha, John Robinson. PLOS One, 2015, Published: May 7, 2015 DOI: 10.1371/journal.pone.0126744. Access the report here.
A January 2014 industrial accident contaminated the public water supply of approximately 300,000 homes in and near Charleston, West Virginia (USA) with low levels of a strongly-smelling substance consisting principally of 4-methylcyclohexane methanol (MCHM). The ensuing state of emergency closed schools and businesses. Hundreds of people sought medical care for symptoms they related to the incident. We surveyed 498 households by telephone to assess the episode’s health and economic impact as well as public perception of risk communication by responsible officials. Thirty two percent of households (159/498) reported someone with illness believed to be related to the chemical spill, chiefly dermatological or gastrointestinal symptoms. Respondents experienced more frequent symptoms of psychological distress during and within 30 days of the emergency than 90 days later. Sixty-seven respondent households (13%) had someone miss work because of the crisis, missing a median of 3 days of work. Of 443 households reporting extra expenses due to the crisis, 46% spent less than $100, while 10% spent over $500 (estimated average about $206). More than 80% (401/485) households learned of the spill the same day it occurred. More than 2/3 of households complied fully with “do not use” orders that were issued; only 8% reported drinking water against advice. Household assessments of official communications varied by source, with local officials receiving an average “B” rating, whereas some federal and water company communication received a “D” grade. More than 90% of households obtained safe water from distribution centers or stores during the emergency. We conclude that the spill had major economic impact with substantial numbers of individuals reporting incident-related illnesses and psychological distress. Authorities were successful supplying emergency drinking water, but less so with risk communication.
Toxicity Assessment of 4-Methyl-1-cyclohexanemethanol and Its Metabolites in Response to a Recent Chemical Spill in West Virginia, USA. Jiaqi Lan , Man Hu , Ce Gao , Akram Alshawabkeh , and April Z. Gu. Environ. Sci. Technol., 2015, 49 (10), pp 6284–6293. Access this report here.
The large-scale chemical spill on January 9, 2014 from coal processing and cleaning storage tanks of Freedom Industries in Charleston affected the drinking water supply to 300,000 people in Charleston, West Virginia metropolitan, while the short-term and long-term health impacts remain largely unknown and need to be assessed and monitored. There is a lack of publically available toxicological information for the main contaminant 4-methyl-1-cyclohexanemethanol (4-MCHM). Particularly, little is known about 4-MCHM metabolites and their toxicity. This study reports timely and original results of the mechanistic toxicity assessment of 4-MCHM and its metabolites via a newly developed quantitative toxicogenomics approach, employing proteomics analysis in yeast cells and transcriptional analysis in human cells. These results suggested that, although 4-MCHM is considered only moderately toxic based on the previous limited acute toxicity evaluation, 4-MCHM metabolites were likely more toxic than 4-MCHM in both yeast and human cells, with different toxicity profiles and potential mechanisms. In the yeast library, 4-MCHM mainly induced chemical stress related to transmembrane transport and transporter activity, while 4-MCHM metabolites of S9 mainly induced oxidative stress related to antioxidant activity and oxidoreductase activity. With human A549 cells, 4-MCHM mainly induced DNA damage-related biomarkers, which indicates that 4-MCHM is related to genotoxicity due to its DNA damage effect on human cells and therefore warrants further chronic carcinogenesis evaluation.
4-Methylcyclohexane methanol. William E. Luttrell. Journal of Chemical Health and Safety, 2015, 22 (1), pp 39–41. Access this report here.
Consumer panel estimates of odor thresholds for crude 4-methylcyclohexanemethanol. McGuire, Michael J.; Suffet, I.H. (Mel); Rosen, Jeffrey. Journal of the American Water Works Association. October 2014. Volume / Number: 106, Number 10, E445-E458. Access this report here.
On Jan. 9, 2014, a spill of “crude” 4-methylcyclohexanemethanol (MCHM) into the Elk River in West Virginia contaminated the water supply for 300,000 people. The crude MCHM caused an intense licorice odor in the drinking water that supplied the area in and around Charleston, W.Va. A sensitive analytical method developed by a commercial laboratory was used to verify the concentrations of crude MCHM presented to a consumer panel selected using specific criteria. The method used for the panel studies was ASTM E679-04, which has been used to determine other odor thresholds in water. The odor threshold and odor recognition concentrations for crude MCHM in water were estimated by the consumer panel to be 0.55 and 7.4 µg/L, respectively. Two estimates of the odor objection concentration were 7.7 and 8.8 µg/L.
Tale of Two Isomers: Complexities of Human Odor Perception for cis- and trans-4-Methylcyclohexane Methanol from the Chemical Spill in West Virginia. Daniel L. Gallagher, Katherine Phetxumphou, Elizabeth Smiley, and Andrea M. Dietrich (Virginia Tech). Environmental Science & Technology, 2015, 49 (3), pp 1319–1327. Access this report here.
Application of gas chromatography with mass spectrometric and human olfactory “sniffer” detectors reveals the nature of odorous chemicals from an industrial chemical spill. Crude 4-methylcyclohexane methanol (4-MCHM) spilled in a river and then contaminated drinking water and air for over 300000 consumers living in West Virginia. Olfactory gas chromatography allows investigators to independently measure the odor of chemical components in a mixture. Crude 4-MCHM is comprised of several major cyclohexane components, four of which have distinct isomer pairs. The cis- and trans-4-MCHM isomers are the only components to have distinct odors at the concentrations used in this study. The trans-4-MCHM is the dominant odorant with descriptors of “licorice” and “sweet”. Trans-4-MCHM has an air odor threshold concentration of 0.060 ppb-v (95% CI: 0.040–0.091). The odor threshold concentrations are not influenced by gender or age but are lower by a factor of 5 for individuals with prior exposure compared to naïve subjects. Individual trans-4-MCHM odor threshold concentrations vary by more than a factor of 100. The cis-4-MCHM isomer has approximately a 2000-fold higher odor threshold concentration, different descriptors, and an even wider individual response range.
Partitioning, Aqueous Solubility, and Dipole Moment Data for cis- and trans-(4-Methylcyclohexyl) methanol, Principal Contaminants of the West Virginia Chemical Spill. Andrea M. Dietrich, Ashly Thomas, Yang Zhao, Elizabeth Smiley, Narasimhamurthy Shanaiah, Megan Ahart, Katherine A. Charbonnet, Nathan J. DeYonker, William A. Alexander, and Daniel L. Gallagher (Virginia Tech and University of Memphis). Environmental Science & Technology Letters. Access this report here.
In 2014, the U.S. National Response Center recorded more than 30000 incidents of oil spills, chemical releases, or maritime security issues, including crude (4-methylcyclohexyl) methanol (MCHM) that contaminated river and drinking water in West Virginia. This research yielded physicochemical partitioning data for the two major compounds released in West Virginia, cis- and trans-(4-methylcyclohexyl)methanol. Octanol–water partition coefficients (KOW) were 225 for cis-4-MCHM and 291 for trans-4-MCHM. The aqueous solubility for total 4-MCHM was 2250 mg/L at 23 °C; solubilities of individual isomers were dependent on their mole fractions. The cis isomer was more soluble and less well sorbed to activated carbon than the trans isomer, consistent with its lower KOW. The partition behavior is supported by a larger computed solvated dipole moment for the cis form than for the trans form at the MP2 aug-cc-pwCVDZ SMD level of theory. Different partition properties would result in the differential fate and transport of cis- and trans-4-MCHM in aqueous environments.
Investigation of MCHM transport mechanisms and fate: Implications for coal beneficiation. Y. Thomas He, Aaron Noble, Paul Ziemkiewicz (West Virginia University). Chemosphere. Volume 127, May 2015, Pages 158–163. Access this report here.
4-Methyl cyclohexane methanol (MCHM) is a flotation reagent often used in fine coal beneficiation and notably involved in the January 9, 2014 Elk River chemical spill in Charleston, WV. This study investigates the mechanisms controlling the transport and fate of MCHM in coal beneficiation plants and surrounding environments. Processes such as volatilization, sorption, and leaching were evaluated through laboratory batch and column experiments. The results indicate volatilization and sorption are important mechanisms which influence the removal of MCHM from water, with sorption being the most significant removal mechanism over short time scales (<1 h). Additionally, leaching experiments show both coal and tailings have high affinity for MCHM, and this reagent does not desorb readily. Overall, the results from these experiments indicate that MCHM is either volatilized or sorbed during coal beneficiation, and it is not likely to transport out of coal beneficiation plant. Thus, use of MCHM in coal beneficiation plant is not likely to pose threat to either surface or groundwater under normal operating conditions.
Determination of (4-methylcyclohexyl)methanol isomers by heated purge-and-trap GC/MS in water samples from the 2014 Elk River, West Virginia, chemical spill. William T. Foreman, Donna L. Rose, Douglas B. Chambers, Angela S. Crain, Lucinda K. Murtagh, Haresh Thakellapalli, Kung K. Wang (USGS and West Virginia University). Chemosphere. 2014.
(DOWNLOAD FOR FREE, Open Access) Access this report here.
A heated purge-and-trap gas chromatography/mass spectrometry method was used to determine the cis- and trans-isomers of (4-methylcyclohexyl)methanol (4-MCHM), the reported major component of the Crude MCHM/Dowanol™ PPh glycol ether material spilled into the Elk River upriver from Charleston, West Virginia, on January 9, 2014. The trans-isomer eluted first and method detection limits were 0.16-μg L−1trans-, 0.28-μg L−1cis-, and 0.4-μg L−1 Total (total response of isomers) 4-MCHM. Estimated concentrations in the spill source material were 491-g L−1trans- and 277-g L−1cis-4-MCHM, the sum constituting 84% of the source material assuming its density equaled 4-MCHM. Elk River samples collected ⩽ 3.2 km downriver from the spill on January 15 had low (⩽2.9 μg L−1 Total) 4-MCHM concentrations, whereas the isomers were not detected in samples collected 2 d earlier at the same sites. Similar 4-MCHM concentrations (range 4.2–5.5 μg L−1 Total) occurred for samples of the Ohio River at Louisville, Kentucky, on January 17, ∼630 km downriver from the spill. Total 4-MCHM concentrations in Charleston, WV, office tap water decreased from 129 μg L−1 on January 27 to 2.2 μg L−1 on February 3, but remained detectable in tap samples through final collection on February 25 indicating some persistence of 4-MCHM within the water distribution system. One isomer of methyl 4-methylcyclohexanecarboxylate was detected in all Ohio River and tap water samples, and both isomers were detected in the source material spilled.
Modeling the Fate and Transport of a Chemical Spill in the Elk River, West Virginia. Bahadur, R. and Samuels, W (Center for Water Science and Engineering). (2014). Journal of Environmental Engineering. Access this report here.
On January 9, 2014, an estimated 37,854 L (10,000 gal.) of 4-methycyclohexane methanol (MCHM) and propylene glycol phenyl ether, solvents used in coal processing, leaked from a ruptured container into the Elk River. The spill, just 1.61 km (1 mi) upstream from a water-treatment plant, forced officials to ban residents and businesses in nine West Virginia counties from using the water for anything other than flushing toilets or fighting fires. An estimated 300,000 West Virginia residents were affected by the spill. This paper reports on the modeling efforts undertaken to forecast time of travel and concentration of MCHM as the plume traveled downstream toward the Greater Cincinnati Water Works (GCWW) intake. The issues addressed include the flow regime, source term describing the spill event, use of real-time and forecast streamflow, and comparison of model results with observations at Charleston (West Virginia), Huntington (West Virginia), and the GCWW intake. The incident-command tool for drinking-water protection (ICWater) was used to model time of travel and concentration of MCHM. Downstream tracing was initiated at the spill site to forecast the location of the leading edge, peak concentration, and trailing edge of the plume for drinking-water intakes as far downstream as 402 km (250 mi).
Modeling of the Elk river spill 2014. Lucien Stolze, Federico Volpin (Technical University of Denmark). Environmental Science and Pollution Research. March 2015. Access this report here.
A dispersion-advection model was used to simulate the Elk river chemical spill 2014. The numerical and analytical solutions were used to predict the concentrations of 4-methylcyclohexane methanol (MCHM) at the water treatment plants located along the Elk and Kanawha rivers. The results are of similar magnitude as measured concentrations although a time-lag was found between modeled and measured plume arrival likely due to accumulation of systematic errors. Considering MCHM guidelines for drinking water, the spill represented a serious health threat through the water up taken by the treatment plant located on the Elk river and it also constituted a risk of contamination for the drinking water produced by treatment plants located on the Kanawha river.
What We’ve Learned From the West Virginia Water Crisis. AJ Whelton, R Gupta. 2014. National Society of Professional Engineers Magazine. Access this here or here PE News Magazine Op-Ed.
Crisis and Emergency Risk Communication: Lessons from the Elk River Spill. John Manuel. Environmental Health Perspectives. 2014 Aug; 122(8): A214–A219. Access this here.
Re-Emergence of Emerging Contaminants. Jerald L. Schnoor. Environmental Science & Technology 2014, 48 (19), 11019–11020. Access this here.
Responding to Crisis: The West Virginia Chemical Spill. William J. Cooper. Environmental Science & Technology. 2014, 48 (6), pp 3095–3095. Access this here.
Chemical Spill in West Virginia Triggers More Studies to Understand Contaminants. Randy Showstack. Transactions American Geophysical Union. Volume 95, Issue 7, pages 61–63, 18 February 2014. Access this here.
The Elk River MCHM Spill: A Cast Study in Managing Environmental Risks. Lucas Rojas Mendoza. InsuranceNewsNet. May 6, 2015. Access thishere.
Questions and comments about this post should be directed to Professor Andrew Whelton at firstname.lastname@example.org.
—This post may be updated as more information becomes available—
On February 12, Dr. Whelton delivered a 60 minute presentation regarding the West Va. Chemical Spill Response and Recovery to attendees of the Indiana Stormwater and Drainage Conference. The event was held in West Lafayette, Indiana and was attended by State regulators, infrastructure and environmental professionals from municipalities, surveyors, and representatives from the infrastructure and environmental design, build, and maintenance industry. Several questions were raised by the audience some of which include “Did Freedom Industries have secondary containment onsite? How much liquid did the failed tank hold? Is the CDC approaching their responsibilities differently seeing that people were harmed by flushing contaminated water into their homes?”
The title of the presentation was Failing to Contain a Spill Upstream of a Drinking Water Intake: Lessons Learned from the Freedom Industries Chemical Spill. A copy of the presentation can be downloaded here: Whelton Storm presentation February 2015. Additional information about detecting, investigating, and recovering from contamination events will be posted in the coming months.
On February 10, Dr. Whelton delivered a presentation at the U.S. Environmental Protection Agency’s Cincinnati, Ohio office at the invitation of NCET (Network for Cincinnati EPA Trainee) Program. The title of the presentation was Drinking Water Plumbing Systems: Green Buildings and Chemical Contamination. The presentation described two different U.S. National Science Foundation (NSF) research projects. One being his team’s past and ongoing research pertaining to the West Virginia chemical spill and the second project pertaining to their investigation of drinking water quality in plastic plumbing systems in the U.S. A copy of the presentation can be downloaded here: Whelton EPA presentation February 2015. A few slides were added to this file following his presentation. These slides include links to his team’s recently published scientific papers about these topics. Additional information about these research activities will be posted in the coming months.
For many months, our University students and faculty colleagues have been hard at work conducting new laboratory experiments and extensively analyzing Freedom Industries chemical spill data. Below are published reports (that I am aware of) regarding the West Virginia chemical spill. If you know of more reports or publicly available testimony due to litigation please send me the links and I’ll post them.
My team continue’s to conduct additional follow-up experiments and these will be announced on Twitter (@TheWheltonGroup) and posted here when completed.
The journal of Environmental Science & Technology accepted our peer-review report. The journal published this manuscript on their website. This document, “Residential Tap Water Contamination….” is available and the website information is listed below. If you are interested in what happened during and since January 9, 2014, you really should read this publication. In addition to an analysis of human health impact data, tap water quality, and flushing data, a very detailed timeline will accompany the report.
Related Scientific Reports and Events
Below we have listed a number of activities we along with other researchers have participated in following the Freedom Industries chemical spill. The items listed below include scientific reports, presentations, town hall meetings, a public forum held at Purdue University, and even an OP-ED. We have also listed links to other documents that have been publicly released by other organizations.
Related 2014 Scientific Reports
American Chemical Society journal of Environmental Science & Technology
In-Home Tap Water Sampling Plan. 2014. Rosen et al.
Crude MCHM Oxidation Study Technical Memo. 2014. McGuire et al.
Investigation of Tentatively Identified Compounds. 2014. Eaton et al.
Health Effects Expert Panel Report. 2014. Dourson et al.
[OUR STUDY] 10 Home Study: Tap water chemical analysis report. 2014. Whelton et al.
[OUR STUDY] 10 Home Study: Resident behavior, perceptions, and residence characteristics report. 2014. Whelton et al.
Consumer Panel Technical Memorandum. 2014. McGuire et al.
Technical Memorandum: Expert Panel Estimates of the Odor Threshold Concentration, Odor Recognition Concentration and Odor Objection Concentration for Crude methylcyclohexanemethanol in Water. 2014. McGuire et al.
[OUR STUDY] Literature Review: Health Effects for Chemicals in 2014 West Virginia Chemical Release: Crude MCHM Compounds, PPH and DiPPH. 2014. Adams et al.
There are also reports from the EPA, CDC, West Va. State Agencies, and Freedom Industries consultants. Many of these are cited in the soon to be published report from our team. Check back soon.
Our Presentations to the Public, Universities, Public Health, Water Industry, and Journalism Professionals
Defining Indiana’s Water Needs: Research and Solutions, Indianapolis, Indiana
Society of Risk Analysis Conference. Denver, Colorado
Evergreen Arts and Humanities Series of Washington State Community College. Marietta, Ohio
Department of Civil and Environmental Engineering. UMASS-Amherst. Amherst, Massachusetts
U.S. Chemical Safety and Hazard Investigation Board. Washington, D.C.
American Water Works Association (AWWA) Water Quality Technology Conference. New Orleans, Louisiana
Civil Engineering Hydraulics Program, Purdue University. West Lafayette, Indiana
AWWA Alabama Mississippi Section Annual Conference. Point Clear, Alabama
AWWA Water Infrastructure Conference. Atlanta, Georgia
Society of the Environmental Journalists Annual Conference. New Orleans, Louisiana
AWWA New England Section Annual Conference. Rockport, Maine
National Association of City and County Health Officials (NACCHO) Annual Conference. Atlanta, Georgia
Division of Environmental and Ecological Engineering. Purdue University. West Lafayette, Indiana
Advanced Material Research Institute. University of New Orleans, New Orleans, Louisiana
American Chemical Society’s Environmental Science & Technology journal. Mar. 2014. Prof. William Cooper, Program Manager National Science Foundation. Responding to Crisis: The West Virginia Chemical Spill http://pubs.acs.org/doi/abs/10.1021/es500949g
Our Participation in Public Forums, Educational Media, and Town Hall Meetings
“Science Nation” public service segment for the US National Science Foundation. In progress
Communications, Community, and Science: The Freedom Industries Chemical Spill Public Forum. West Lafayette, Indiana. Nov. 2014.
WVTAP public meeting. Charleston, West Virginia. Mar. 2014.
Ohio Valley Environmental Coalition (OVEC) sponsored town hall meetings at Marshall University in Huntington, WV and Putnam County, WV. Feb. 2014.
YouTube.com plumbing system flushing video developed for West Virginia residents by Krista Bryson, Ohio State University. Posted online at West Virginia Water Crisis: Exclusive *Crucial* Information about Flushing. Jan. 2014. https://www.youtube.com/watch?v=Rz3Y7rjnqEs
Blog posting at the West Virginia Water Crisis Blog. Your Questions Answered: Flushing Recommendations, Water and Water Systems Safety, and Health Concerns. Jan. 2014. www.wvwatercrisis.com
Who Has or is Researching Issues Surrounding this Spill?
Below is a list of which organizations have or are currently conducting research in response to the Freedom Industries chemical spill. If you know of others, please email us and we will update this list. We tried to breakout the types of research into general categories. Some research teams are working on multiple topics. The organizations are listed alphabetically.
Risk Communication, Social, and Behavioral Impacts
Corona Environmental Consulting, Georgetown University, Harvard University, Ohio State University, Purdue University, University of Charleston, University of Kentucky, University Wisconsin-Madison
Environmental Sampling, Monitoring, and Modeling
Corona Environmental Consulting, Purdue University, Technical University of Denmark, University of Memphis, USGS, Virginia Tech, West Virginia University
Water Infrastructure Issues
Corona Environmental Consulting, Eurofins Eaton Analytical, Purdue University, McGuire Inc., UCLA, Utah State University, Virginia Tech, West Virginia University
NIH National Toxicology Program, Northeastern University, Purdue University, TERA, University of South Alabama, Utah State University, USGS
Over the past couple years we have tested many different brands of plastic pipe to determine the degree these plumbing materials can alter drinking water quality. We have also characterized drinking water from plastic plumbing systems in six States. This work continues to be funded by the US National Science Foundation (NSF) to enable us to better understand the phenomena that control the in-home drinking water quality.
Please browse below and contact us if you have any questions. Above all, we believe that it is important that transparent plumbing system material testing data be available so that construction professionals and homeowners can make the best material selection decision for their clients and themselves.
Contact Us if you have any questions at email@example.com.
What We Tested during 1 Month Exposure of New Pipes
1. Ability of each material to:
Leach chemicals that promote bacteria growth in plumbing systems
Leach chemicals that have existing health limits
Cause the drinking water to have an odor
Leach chemicals that can be transformed into carcinogenic byproducts that have health limits
Leach chemicals that do not have existing health limits
2. Each material’s resistance to degradation and resistance to permeation
3. Each material’s ability to reduce chlorine disinfectant level
4. The role of chlorine disinfectant on affecting the drinking water chemical and odor impacts
NOTE: All materials we have tested are available in US building supply stores. All materials tested had been certified by the nonprofit organization, National Sanitation Foundation International (NSFI) Standard 61.
Location of the In-Home PEX Plumbing Systems We Tested
We also determined how pipe leaching can be affected by the cleaning method required by building code and the plumber.
Over the next several months more of our testing results will be made available. Many reports and publications have already been published and presented.
We will be presenting some of these results at the USGBC GreenBuild Conference in New Orleans, LA here. Dr. Alexandra Stenson and Andrew Whelton are principal investigators on the NSF project. Rebecca Bryant, Managing Principal of Watershed, LLC is also one of the project leaders.
The National Society of Professional Engineers (NSPE) published our OP-ED in their August/September NSPE Magazine. The submission described part of our efforts following the 2014 West Virginia large-scale drinking water contamination disaster. Specifically, eight lessons learned were discussed. The NSPE website can be found here and a copy of the PDF OP-ED can be found here: Download the NSPE OPED WheltonGupta (2014) here).
Results of this OP-ED were made possible because of the contributions of many people. Students LaKia McMillan, Matt Connell, Jeff Gill, Keven Kelley, Caroline Novy, Jesus Estaba, Freddie Avera, Maryam Salehi, and Professor Kevin White are greatly appreciated. Funding for some of the effort conducted was provided to us by the US National Science Foundation and State of West Virginia. We also had the privilege of working with Corona Environmental Consulting President Jeffrey Rosen, along with Ayhaun Ergul, Jennifer Clancy, Tim Clancy, Tim Bartrand, Toxicological Excellence in Risk Assessment Executive director Mike Dourson and Jacqueline Patterson, Utah State University Professor Craig Adams, CEO Michael J. McGuire, along with many other experts from West Virginia, across the US, Israel, and the UK.
Late Monday afternoon August 4, the City of Toledo released their Preliminary Water Crisis Study Report. This report describes some of the data and actions taken during the recent large-scale tap water contamination incident. Earlier in the day, the Mayor of Toledo declared tap water safe to drink for the entire 500,000 person area. The Toledo-Lucas County Health Department then issued guidance to residents and businesses on how to flush their plumbing systems.
I provided some thoughts about their report below mainly focusing on tap water contamination response and recovery. In short, their preliminary report does not address many questions pertaining to the degree scientific principles were considered in water use, water testing, and flushing recommendations. The report also does not answer many of the public’s remaining questions. For an incident that affected 500,000 people, residents being told to flush contaminated water into their homes, and that the new water is safe, the lack of information provided by officials as of today is remarkable. Hopefully someone explains what happened and what data they used to make decisions in the coming days.
Who actually was involved in the response and decisions remains somewhat of a mystery
The report cites the Mayor, City of Toledo, Toledo-Lucas County Health Department, the Oregon treatment plant, Lake Superior University, Ohio EPA Columbus, and US EPA Cincinnati, but has no mention of CDC. According to the report the organizations listed above were the only organizations that had a hand in the data collection, analysis, reporting, and decision making process. Publicly, the health department proclaimed CDC was involved during an interview. But CDC was not listed in the City of Toledo report? Who was involved and what advice did they provide? This is important information as it can clarify why certain decisions were made and who provided information. I know many folks in the drinking water industry including other water companies and experts that contacted Ohio organizations involved and offered assistance. From what I understand, responders did not accept any assistance except from the few organizations listed above. Even so, they seem to have had contact with other organizations they did not disclose in their report (i.e., CDC).
Did officials mislead the public? It was really a Do Not Use order for some of the residents
The report portrays the responders considering the incident as a Do Not Drink /Do Not Boil Order, but that is not quite accurate. After issuing the Do Not Drink/Do Not Boil Order, the Toledo-Lucas County Health Department actually went further and publicly advised immunocompromised persons, children, and breastfeeding individuals not to have any contact with the water. That’s not a Do Not Drink Order. That’s a Do Not Use Order more similar to what was issued in West Virginia following the Crude MCHM Chemical Spill where 300,000 people were denied access to tap water for up to 10 days. The Toledo-Lucas County Health Department also advised people it was okay to brush their teeth with the contaminated water, then pulled back on that recommendation a day later. These conflicting messages implied that the responders were creating guidance on the fly, and/or did not understand what a Do Not Drink Order was. The media kept reporting Do Not Drink orders, but the Health Department was advising the population to do more than simply not drink the water. The incident was a Do Not Use order for some people not just a Do Not Drink /Do Not Boil order.
Some of the reported microcystin data could be suspect because of water collection practices. It was a good decision to use multiple labs.
Water samples that were shipped to Lake Superior State University had chlorine residual present. Microcystin (toxin) is known to react and degrade (and transform into other compounds) when exposed to chlorine. Thus, during shipping some of the toxin could have been destroyed or transformed into other compounds. To limit these changes, chlorine residual neutralization should have been considered once the water was collected. No justification of why samples were allowed to react with chlorine during transport (or not) was provided. Microcystin experts reading this will likely have more insight into the analytical methods. Kudos to Lake Superior State University for their work on this effort. Great to see independent experts involved. It would be helpful if officials could explain their methods.
Were the water samples collected representative of the highest chemical levels in the water system and at exposure locations?
During a quick response, responders generally collect water at easy to access locations such as at the source (i.e., Lake Erie), water plant, and within in the water distribution system (i.e., hydrants, restaurants, etc). This information is important to understand the scale of contamination (where the tainted water is). After tap water leaves the treatment plant, it does however take tap water different times to travel to different parts of the community so some tap water may be newer in certain other parts of the water system. Why were certain water distribution system locations selected for sampling? Do they represent the entire water system or are they biased? Reasoning why the certain locations were selected was not provided in the report. Did the responders sample to find out the highest chemical levels in the water distribution system? Were they representative?
Also important to point out is that tap water quality at a fire hydrant is not necessarily the same as tap water quality in a residential building. It remains unclear if responders tested in-home locations. [BP Gas station plumbing systems are not the same as two story home plumbing systems, dormitories, or apartment complexes].Restaurants, government buildings, hydrants, gas stations, etc. were some of the tap water collection points. This is similar to West Virginia’s initial response. West Virginia only tested hydrants, government buildings, and businesses. But, the question everyone asked in West Virginia that turned out to be important was what chemical levels were in found at the exposure points….within people’s homes?
If Toledo learned from West Virginia, they would have considered sampling in homes. What did they do and why did they do it?
The plumbing system flushing protocol was never tested before residents were told to partake
The ability of the flushing protocol to reduce chemical levels within homes was never tested. The reason for this decision by the responders was not described in the report. Moreover, no personal safety guidance was provided to residents about how to avoid tap water chemical exposure during flushing. Was it okay to flush hot water with your children in the room or house? (see below for some scientific analysis)
The Toledo-Lucas County Health Department plumbing system flushing guidelines were nearly identical to those used in West Virginia (where people experienced acute chemical exposure symptoms while following those guidelines). Similar to West Virginia’s flushing guidelines, the Toledo-Lucas County Health Department guidelines are also similar to those when tap water with high levels of pipe corrosion products such lead and copper needs to be removed from plumbing systems. Water utilities have a long history of flushing certain chemicals out of their system to include lead, copper, iron, sediment, etc. I am not aware of any existing protocols for flushing microcystin contaminated tap water from homes however. This could be the first. What conditions would have been needed for officials to “test” the protocol before directing residents to partake?
There are key differences between the Toledo and West Virginia tap water contamination incidents that pertaining to flushing. Chemicals in West Virginia’s tap water were volatile meaning that they would readily evaporate from water into air. When West Virginians opened their taps to flush contaminated tap water, chemicals volatilized into the air. Flushing hot water in West Virginia exacerbated this problem. Many homes in West Virginia my team visited had poor ventilation bathrooms and chemically contaminated air accumulated. Like the West Virginia incident, hot water flushing was recommended in Toledo. But, in Toledo, microcystin (and likely its degradation products) were much less volatile. So, the probability of chemicals in Toledo’s water evaporating into air was much less. Still, should hot water flushing been recommended in Ohio knowing that organic chemicals volatilize into air faster than cold water?
As of August 5, no increased reports of acute chemical exposure symptoms had been reported in the Toledo area which is a good sign. I hope they address this topic in the coming days.
The Toledo incident again demonstrates that in the US, large portions of our population can be denied access to safe tap water and responding to contamination incidents is very complex. Seven months ago 15% of the people who live in West Virginia experienced something very similar.
I have no doubt officials responding to the Toledo incident worked very long hours, likely days without sleep and sacrificed many hours away from family and friends to help. We will never know the names of many of these individuals, but they should be widely thanked for their service in helping investigate and recover the community from this incident. These individuals helped out because they care about the health and welfare of the community similar to what I witnessed in West Virginia.
Several hours after the City Council meeting we have a little more information, but not much. According to the City of Toledo, EPA still has not released all of their data. There were tremendous data release delays by Federal government agencies during the West Virginia crisis. Federal agencies, from my perspective, were at times completely detached from the timeline of people who lived through the incident. The State of West Virginia requested numerous times for Federal agencies to provide data and results took months to obtain. Federal agencies were on their own timetable. Will that be the case in Ohio?
If residents affected by this incident are to feel confident in their tap water and officials, they need and deserve answers soon. If the Nation is to learn from this incident, more information must be made public. While there clearly is a need for improved nutrient control near Lake Erie, communities across the Nation can benefit from learning about the good and bad of this large-scale tap water contamination response. It’s inevitable; We all need safe tap water and these incidents will happen again.
Andrew Whelton, Ph.D.
NOTE: This post could be revised if information is brought to my attention requiring the post to be revised. Revision explanations, if any, will be posted at the bottom of the page.